Découvrez les évènements passés et à venir dans le monde entier et en ligne, qu’ils soient organisés par le CIFOR-ICRAF ou auxquels participent nos chercheurs.

{{menu_nowledge_desc}}.

CIFOR–ICRAF publishes over 750 publications every year on agroforestry, forests and climate change, landscape restoration, rights, forest policy and much more – in multiple languages.

CIFOR–ICRAF addresses local challenges and opportunities while providing solutions to global problems for forests, landscapes, people and the planet.

We deliver actionable evidence and solutions to transform how land is used and how food is produced: conserving and restoring ecosystems, responding to the global climate, malnutrition, biodiversity and desertification crises. In short, improving people’s lives.

Impact of land change on aboveground tree carbon stocks in the Taita Hills, Kenya

Export citation

Land use change refers to the modification of the Earth’s surface by humans. Land use/land cover change (in short land change) especially the clearing of tree cover is a major source of increased carbon dioxide (CO2) emissions contributing to anthropogenic climate change. In this study carbon densities and changes in aboveground tree carbon (agc) across different land cover types were mapped in the Taita Hills Kenya using field measurements airborne laser scanning (ALS) data and classified satellite imagery. An existing biomass map was used for retrieving carbon densities for a part of the study area. For the lowland area another biomass map was created with a regression model based on field measurements of 415 trees on 61 plots and metrics calculated from discrete return ALS data. Explanatory variables in the linear regression model were the standard deviation and 60 % height percentiles of return elevations. Carbon fraction was calculated as 47 % of aboveground biomass. 11 land cover classes were classified from a satellite image with an object-based approach. Overall classification accuracy was 71.1 % with most confusion between the cropland and shrubland classes and shrubland and thicket. Based on the biomass maps carbon densities were calculated for different land cover classes. Mean carbon densities were 89.0 Mg C ha-1 for indigenous broadleaved forests 29.0 Mg C ha-1 for plantation forests 15.6 Mg C ha-1 for woodland 5.5 Mg C ha-1 for thicket 3.2 Mg C ha-1 for shrubland 8.1 Mg C ha-1 for croplands above 1220 meters above sea level (m a.s.l.) and 2.3 Mg C ha-1 for croplands below 1220 m a.s.l.. Land cover maps from 1987 1992 2003 and 2011 were used for studying the impact of land change on aboveground carbon stocks. A reduction in carbon storage was observed between years 1987 1992 and 2003. An increase in total carbon stocks from 2003 to 2011 was observed as a results of increased proportion of woodland plantation forest and broadleaved forest. These changes should be further verified in a spatially explicit way. More detailed data should be used in order to understand the full complexity of the dynamics between land change and carbon stocks in the heterogeneous landscape of the Taita Hills.

Related publications